Bhatt Manish, Zhao Jian-Shen, Halasz Annamaria, Hawari Jalal
Biotechnology Research Institute, National Research Council of Canada, Montreal, QC, Canada H4P 2R2.
J Ind Microbiol Biotechnol. 2006 Oct;33(10):850-8. doi: 10.1007/s10295-006-0136-x. Epub 2006 May 16.
Undersea deposition of unexploded ordnance (UXO) constitutes a potential source of contamination of marine environments by hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) and octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX). Using sediment from a coastal UXO field, Oahu Island, Hawaii, we isolated four novel aerobic RDX-degrading fungi HAW-OCF1, HAW-OCF2, HAW-OCF3 and HAW-OCF5, tentatively identified as members of Rhodotorula, Bullera, Acremonium and Penicillium, respectively. The four isolates mineralized 15-34% of RDX in 58 days as determined by liberated 14CO2. Subsequently we selected Acremonium to determine biotransformation pathway(s) of RDX in more details. When RDX (100 microM) was incubated with resting cells of Acremonium we detected methylenedinitramine (MEDINA), N2O and HCHO. Also we detected hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine (MNX) together with trace amounts of hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine (DNX) and hexahydro-1,3,5-trinitroso-1,3,5-triazine (TNX). Under the same conditions MNX produced N2O and HCHO together with trace amounts of DNX and TNX, but we were unable to detect MEDINA. TNX did not degrade with Acremonium. These experimental findings suggested that RDX degraded via at least two major initial routes; one route involved direct ring cleavage to MEDINA and another involved reduction to MNX prior to ring cleavage. Nitrite was only detected in trace amounts suggesting that degradation via initial denitration did take place but not significantly. Aerobic incubation of Acremonium in sediment contaminated with RDX led to enhanced removal of the nitramine.
未爆炸弹药(UXO)在海底的沉积构成了六氢-1,3,5-三硝基-1,3,5-三嗪(RDX)和八氢-1,3,5,7-四硝基-1,3,5,7-四氮杂环辛烷(HMX)对海洋环境造成污染的潜在来源。我们利用来自夏威夷瓦胡岛沿海未爆炸弹药区域的沉积物,分离出了四种新型的好氧RDX降解真菌HAW-OCF1、HAW-OCF2、HAW-OCF3和HAW-OCF5,初步鉴定它们分别为红酵母属、布勒酵母属、枝顶孢属和青霉属的成员。通过释放的14CO2测定,这四种分离菌株在58天内将15%-34%的RDX矿化。随后,我们选择枝顶孢属来更详细地确定RDX的生物转化途径。当将RDX(100微摩尔)与枝顶孢属的静止细胞一起孵育时,我们检测到了亚甲基二硝胺(MEDINA)、N2O和HCHO。此外,我们还检测到了六氢-1-亚硝基-3,5-二硝基-1,3,5-三嗪(MNX)以及痕量的六氢-1,3-二亚硝基-5-硝基-1,3,5-三嗪(DNX)和六氢-1,3,5-三亚硝基-1,3,5-三嗪(TNX)。在相同条件下,MNX产生了N2O和HCHO以及痕量的DNX和TNX,但我们未能检测到MEDINA。TNX不能被枝顶孢属降解。这些实验结果表明,RDX至少通过两条主要的初始途径降解;一条途径涉及直接开环生成MEDINA,另一条途径涉及在开环之前还原为MNX。仅检测到痕量的亚硝酸盐,这表明通过初始脱硝进行的降解确实发生了,但不显著。在受RDX污染的沉积物中对枝顶孢属进行好氧培养导致硝胺的去除增强。